JPH09299712A - Waste muddy water treatment and device therefor - Google Patents

Waste muddy water treatment and device therefor

Info

Publication number
JPH09299712A
JPH09299712A JP12033896A JP12033896A JPH09299712A JP H09299712 A JPH09299712 A JP H09299712A JP 12033896 A JP12033896 A JP 12033896A JP 12033896 A JP12033896 A JP 12033896A JP H09299712 A JPH09299712 A JP H09299712A
Authority
JP
Japan
Prior art keywords
hose
waste
muddy water
flocs
mud
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP12033896A
Other languages
Japanese (ja)
Inventor
Katsuyuki Tamaoki
克之 玉置
Wataru Aizawa
渉 相澤
Sumio Horiuchi
澄夫 堀内
Tomio Kishino
富夫 岸野
Yoshio Iizuka
芳雄 飯塚
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shimizu Construction Co Ltd
Shimizu Corp
Original Assignee
Shimizu Construction Co Ltd
Shimizu Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shimizu Construction Co Ltd, Shimizu Corp filed Critical Shimizu Construction Co Ltd
Priority to JP12033896A priority Critical patent/JPH09299712A/en
Publication of JPH09299712A publication Critical patent/JPH09299712A/en
Pending legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To effectively separate a mud content such as bentonite from waste muddy water with a small site area by a simple method by adding a flocculant to waste muddy water to mix them before introducing the mixture into a wound hose and making flocs retain there while the flocs formed in the hose is slowly agitated. SOLUTION: After waste muddy water discharged from a construction site such as the shield work one is temporarily stored in a storage tank 1, it is introduced into a static mixer 4 through a flow regulating valve 2 and a flowmeter 3. Organic flocculant solution is added there from a flocculant tank 5, and an inorganic flocculant is added from a flocculant tank 7 in the next mixing pipe 6. Then, when the waste muddy water is introduced into a hose inlet part of a wound hose flock forming device 8, it is slowly passed through the wound hose, and during that time, floc forming reaction is accelerated to sufficiently grow flocs. The flocs and free water are properly separated in the hose in the outlet part and brought out to outside the system. Next, the flocs and the separated water are separated by a gravity dehydrator 9.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、建設現場から排出
される廃棄ベントナイト泥水等の廃棄泥水からベントナ
イト等の泥分を容易にかつ効率的に分離回収する廃棄泥
水処理方法及び装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a waste mud treatment method and apparatus for easily and efficiently separating and recovering mud such as bentonite from waste mud such as waste bentonite mud discharged from a construction site.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】従来、
地中掘削工事としての泥水シールド工法や場所打ち杭工
法等の工法においては、掘削壁面を安定させるためにる
ために、また掘削土を流体搬送するために、一定濃度の
ベントナイト泥水が多量に用いられている。この際の使
用済みの廃棄泥水(廃棄ベントナイト泥水)を直接河川
や下水へ放出することは、環境へ悪影響を及ぼす恐れが
あるため許されず、泥分(ベントナイト分)を分離回収
した後、分離処理水を河川等へ放流しなければならな
い。ところが、泥分(ベントナイト分)は容易に沈降分
離できず、そのまま長期間放置しても、液表面の水分だ
けが蒸発乾燥するのみで、泥分(ベントナイト分)が自
然に分離して沈殿することはない。そこで、廃棄泥水
(廃棄ベントナイト泥水)に凝集剤、例えば無機系凝集
剤としてのポリ塩化アルミニウム(PAC)や硫酸アル
ミニウム、また有機系高分子凝集剤としてのアクリル酸
ソーダ、アクリルアミド等を添加混合した後、自然放置
して(ベントナイト)フロックを沈殿させ、その後濾過
等を行って泥分(ベントナイト分)を分離回収すること
が行われている。また、沈殿槽中でフロックを沈殿させ
る方法も実施されている。
2. Description of the Related Art
In the construction method such as mud shield method and cast-in-place pile method for underground excavation work, a large amount of bentonite mud water with a certain concentration is used to stabilize the excavation wall surface and to transport the excavated soil in fluid. Has been. Direct release of used waste mud (waste bentonite mud) to rivers and sewage at this time is not allowed because it may adversely affect the environment. Water must be discharged into rivers. However, the mud (bentonite) cannot be easily settled and separated, and even if left alone for a long time, only the water on the liquid surface evaporates and dries, and the mud (bentonite) naturally separates and precipitates. There is no such thing. Therefore, after adding and mixing a coagulant, for example, polyaluminum chloride (PAC) or aluminum sulfate as an inorganic coagulant, and sodium acrylate or acrylamide as an organic polymer coagulant to waste mud (disposal bentonite mud), It is carried out that the flocs are left to stand naturally (bentonite) and then the mud (bentonite) is separated and recovered by performing filtration or the like. In addition, a method of precipitating flocs in a settling tank is also practiced.

【0003】しかしながら、凝集剤を添加した後に自然
放置する場合、広大な敷地面積を確保しなければならな
い問題があり、また沈殿槽を使用する方法にあっても大
型の沈殿槽を必要としていた。さらに、遠心分離法やフ
ィルタプレス法等によって固液分離を行う方法も存在す
るが、ケーキ状ベントナイトの後処理工程として多くの
工程を経なければならず、また装置が高価なものとなる
問題がある。また特に、フィルタプレス法や遠心分離法
では、バッチ(回分式)をとる場合が多く、工業的に有
利な連続処理が困難であった。
However, in the case where the coagulant is added and left to stand naturally, there is a problem that a vast site area must be secured, and a method using a sedimentation tank requires a large sedimentation tank. Furthermore, there is also a method of performing solid-liquid separation by a centrifugal separation method, a filter press method, etc., but many steps must be performed as a post-treatment step of cake-like bentonite, and there is a problem that the apparatus becomes expensive. is there. Further, in particular, in the filter press method and the centrifugal separation method, a batch (batch type) is often used, and industrially advantageous continuous treatment is difficult.

【0004】[0004]

【課題を解決するための手段】本発明は、上記課題を解
決するものであり、例えばアースドリル工法等の場所打
ち杭工法により、杭工事終了時点等で発生する少量(約
100m)の廃棄泥水を省スペースのフロック生成装
置で沈降分離処理するようにしたものであり、その結果
廃棄泥水処理装置をコンパクト化することを可能とした
ものである。よって、廃棄泥水処理装置を車載型等の移
動式廃棄泥水処理装置とすることも可能となるものであ
るすなわち本発明は、下記の構成よりなるものである。 (1)廃棄泥水に凝集剤を添加混合した後、それを巻回
ホース中に導入し、同ホース内で生成するフロックをゆ
っくりと撹拌しながら滞留させ、水との分離を促進させ
ることを特徴とする廃棄泥水処理方法。 (2)巻回ホースが、渦巻き状ホースであることを特徴
とする前記(1)項記載の廃棄泥水処理方法。 (3)巻回ホースが、立体的に巻回してなるものであ
り、廃棄泥水を巻回ホースの入口より供給することを特
徴とする(1)項又は(2)項記載の廃棄泥水処理方
法。 (4)巻回ホースよりなるフロック生成装置を備えてな
ることを特徴とする廃棄泥水処理装置。 (5)巻回ホースが、渦巻き状ホースであることを特徴
とする(4)項記載の廃棄泥水処理装置。 (6)巻回ホースが、立体的に巻回してなるものであ
り、廃棄泥水が巻回ホースの入口より供給されることを
特徴とする(4)項又は(5)項記載の廃棄泥水処理装
置。 (7)前記(4)項ないし(6)項のいずれかに記載の
廃棄泥水処理装置を備えてなることを特徴とする移動式
廃棄泥水処理装置。 (8)前記(4)項ないし(6)項のいずれかに記載の
廃棄泥水処理装置を備えてなることを特徴とする車載型
移動式廃棄泥水処理装置。
DISCLOSURE OF THE INVENTION The present invention is to solve the above-mentioned problems, and for example, by a cast-in-place pile construction method such as an earth drill construction method, a small amount (about 100 m 3 ) of waste generated at the end of pile construction is discarded. The muddy water is settled and separated by a space-saving floc generator, and as a result, the waste muddy water treatment device can be made compact. Therefore, the waste muddy water treatment device can be a mobile waste muddy water treatment device such as an on-vehicle type, that is, the present invention has the following configuration. (1) A feature that after adding and mixing a coagulant to waste mud water, introducing the coagulant into a winding hose and allowing flocs generated in the hose to slowly accumulate while agitating to promote separation from water And the waste mud treatment method. (2) The method for treating waste mud water according to the item (1), wherein the wound hose is a spiral hose. (3) The method for treating waste mud water according to item (1) or (2), characterized in that the winding hose is three-dimensionally wound and waste mud is supplied from the inlet of the winding hose. . (4) A waste mud treatment device comprising a floc generation device including a wound hose. (5) The waste mud treatment device according to item (4), wherein the winding hose is a spiral hose. (6) The waste mud treatment according to (4) or (5), wherein the winding hose is three-dimensionally wound, and waste mud is supplied from the inlet of the winding hose. apparatus. (7) A mobile waste mud treatment device comprising the waste mud treatment device according to any one of (4) to (6). (8) An on-vehicle mobile waste sludge treatment device comprising the waste sludge treatment device according to any one of (4) to (6).

【0005】上記発明においては、フロックの良好な生
成・沈降を大型の沈殿槽やフイルタプレス等を使用せず
に、簡易な手段により可能とするもので、単にホースを
巻回してなる部分で実施するのであり、真直に伸ばせば
非常に長い距離となるホースを単に巻回、特に好ましく
は立体的に(上下に)幾重にも巻回して、省スペース化
したフロック生成部(フロック生成装置)を構成してい
る。よって巻回廃棄泥水を単にホースを巻回するという
簡易構造で省スペースのフロック生成装置が構成され、
そこでフロックが良好に生成されるため、簡易な手段で
の固液分離を可能とし、廃棄泥水処理装置をコンパクト
なものとなすことができる。立体的に巻回したホース内
を凝集剤が添加混合された廃棄泥水が通過すると、その
間で緩速撹拌され、フロックの良好な生成が促進され
る。
In the above invention, good flocs can be formed and settled by a simple means without using a large settling tank or a filter press. Therefore, a hose that can be very long if it is straightened is simply wound, particularly preferably three-dimensionally (up and down) in multiple layers to save a space-saving flock generation unit (flock generation device). I am configuring. Therefore, a space-saving floc generation device is configured with a simple structure in which wound hose is simply wound around a hose.
Therefore, flocs are favorably generated, so that solid-liquid separation can be performed by a simple means, and the waste mud treatment device can be made compact. When the waste mud mixed with the coagulant is passed through the three-dimensionally wound hose, the waste mud is slowly agitated during that time, and good floc formation is promoted.

【0006】上記のごとく廃棄泥水処理装置のコンパク
ト化に基づき、特に車載型の移動式廃棄泥水処理装置と
したものにあっては、現場に停車した自動車上あるいは
自動車上から下ろした状態において、廃棄泥水を廃棄泥
水貯留タンクから直接搬送し、車載処理装置内で処理す
ることができ、廃棄泥水からの分離水を下水へ放流し、
濃縮されたフロック状の汚泥は運搬車両に排出すること
ができる。廃棄泥水処理装置内では、廃棄泥水に有機系
凝集剤と無機系凝集剤の2種類の無害な凝集剤(例え
ば、アルギン酸ナトリウムやポリアクリルアミド系のア
ニオン性高分子凝集剤等とアタパルジャイト(MgとA
lの塩基性含水ケイ酸塩鉱物)微粉末凝集剤)を添加混
合し、廃棄泥水中の固形分を凝集させ、粒状のフロック
と分離水に固液分離することが好ましい。こうして、元
の廃棄泥水体積1に対して、2/3量の水と1/3量の
フロック状の濃縮泥分に分離され、このフロック状の濃
縮泥分をダンプ車等へ積載して廃棄場へ移送廃棄する。
Based on the downsizing of the waste muddy water treatment apparatus as described above, particularly in the case of an on-vehicle mobile waste muddy water treatment apparatus, the waste muddy water treatment apparatus is discarded when the vehicle is parked at the site or dropped from the vehicle. Muddy water can be directly transported from the waste muddy water storage tank and processed in the in-vehicle treatment device, and the separated water from the waste muddy water is discharged to sewage,
The concentrated floc-like sludge can be discharged to a transport vehicle. In the waste mud treatment device, two kinds of harmless coagulants (eg, sodium alginate or polyacrylamide anionic polymer coagulant) and attapulgite (Mg and A
It is preferable to add (1) basic hydrous silicate mineral) fine powder aggregating agent) to agglomerate the solid content in the waste mud water and to perform solid-liquid separation into granular flocs and separated water. In this way, with respect to the original waste mud volume of 1, it is separated into 2/3 amount of water and 1/3 amount of floc-like concentrated mud, and the floc-like concentrated mud is loaded on a dump truck or the like and discarded. Transfer to the site and discard.

【0007】凝集剤としては、前記アタパルジャイトの
ほか、ポリ塩化アルミニウム(PAC)、硫酸バンド、
塩化第2鉄等の無機系凝集剤や、前記ポリアクリルアミ
ド系のアニオン性高分子凝集剤、アルギン酸塩等の有機
系凝集剤が使用できる。
As the coagulant, in addition to the attapulgite, polyaluminum chloride (PAC), sulfuric acid band,
An inorganic flocculant such as ferric chloride, the polyacrylamide anionic polymer flocculant, or an organic flocculant such as alginate can be used.

【0008】[0008]

【発明の実施の形態】本発明の実施の形態を図面に基づ
いて説明する。図1は、本発明に係る廃棄泥水処理装置
の概説図であり、図2は、本発明に係る廃棄泥水処理装
置を車載して移動式となした場合の概説図である。図1
においては、まず例えばシールド工法施工現場から排出
される廃棄泥水(廃棄ベントナイト泥水)が貯留された
廃棄泥水貯留槽1から、廃棄泥水が管路を経て導出さ
れ、流量調整弁2及び流量計3を経てスタチックミキサ
ー4に導入される。そこで、凝集剤槽(A剤槽)5から
有機系凝集剤溶液を添加混合し、次いで混合管6におい
て、他の凝集剤槽(B剤槽)7から無機系凝集剤を添加
する。その後、前記2種の凝集剤が添加混合された廃棄
泥水は、本発明に係る巻回ホースフロック生成装置のホ
ース入口部から導入される。巻回ホース内においては、
前記廃棄泥水はゆっくりと通過して行き、その間でフロ
ックの生成反応が促進し、ホース内に生成するフロック
はホース内で十分に成長し、出口部のホース内において
は、フロックと遊離水が良好に分離して系外へ導出され
てくる。次いで、メツシュベルトで構成される重力脱水
装置9へ供給され、生成熟成されたフロックと分離水と
に即座に分別され、メツシュベルト上に残ったフロック
分はベルトプレス型脱水装置10へ移送され、更に脱水
されて脱水ケーキとなり、脱水ケーキはベルトコンベア
11により、ダンプ車等の廃棄物移送車へ積載される。
メツシュベルト型重力脱水装置9から導出される分離水
とベルトプレス型脱水装置10から導出される分離水
は、調整槽12へ導入され、そこでpH測定及びSS測
定され、かつ酸、アルカリ等の添加による中和及び凝集
剤添加によるSS分の除去が図られた後、下水へ放流さ
れる。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a schematic diagram of a waste mud treatment device according to the present invention, and FIG. 2 is a schematic diagram of a case where the waste mud treatment device according to the present invention is mounted on a vehicle and is movable. FIG.
First, for example, waste mud is discharged from a waste mud storage tank 1 in which waste mud (waste bentonite mud) discharged from the shield construction method construction site is stored, through a pipe line, and a flow control valve 2 and a flow meter 3 are connected. After that, it is introduced into the static mixer 4. Therefore, the organic coagulant solution is added and mixed from the coagulant tank (A agent tank) 5, and then the inorganic coagulant is added from the other coagulant tank (B agent tank) 7 in the mixing pipe 6. After that, the waste mud containing the two coagulants added and mixed is introduced from the hose inlet of the wound hose floc generator according to the present invention. In the winding hose,
The waste mud slowly passes through, during which the floc formation reaction is promoted, the flocs generated in the hose grow sufficiently in the hose, and the flocs and free water are good in the outlet hose. It is separated into two and is led out of the system. Then, it is supplied to a gravity dehydrator 9 composed of a mesh belt, and immediately separated into generated and matured flocs and separated water, and the flocs remaining on the mesh belt are transferred to a belt press type dehydrator 10 for further dehydration. As a result, the dehydrated cake is loaded onto the waste transfer vehicle such as a dump truck by the belt conveyor 11.
The separated water derived from the mesh belt type gravity dewatering device 9 and the separated water derived from the belt press type dewatering device 10 are introduced into the adjusting tank 12, where pH measurement and SS measurement are performed, and by addition of acid, alkali and the like. After the SS content is removed by neutralization and addition of a coagulant, it is discharged into sewage.

【0009】図2に示す車載型移動式廃棄泥水処理装置
14においては、廃棄泥水貯留槽1から導出された廃棄
泥水はスタチックミキサー4内でA凝集剤が添加混合さ
れ、次いで混合管6内で凝集剤Bが添加され、その後巻
回ホースフロック生成装置8の入口部に導入され、かつ
ホース内をゆっくりと通過する。そのホース内ではフロ
ックの生成反応が促進し、ホース内に生成するフロック
はホース内で十分に成長し、出口のホース内において
は、フロックと遊離水が良好に分離して系外へ導出さ
れ、その後、重力脱水装置9へ供給され、フロックと分
離水とに分別され、重力脱水装置のメツシュベルト上に
残ったフロック分はベルトプレス型脱水装置10へ移送
され、更に脱水されて脱水ケーキとなり、脱水ケーキは
ベルトコンベア11により、ダンプ車等の廃棄物移送車
13へ積載される。メツシュベルト型重力脱水装置9か
ら導出される分離水とベルトプレス型脱水装置10から
導出される分離水は、調整槽12へ導入され、そこでp
H測定及びSS測定され、かつ酸、アルカリ等の添加に
よる中和及び凝集剤添加によるSS分の除去が図られた
後、下水へ放流される。なお、以上に説明した本発明の
廃棄泥水の固液分離処理方法及び処理装置は、他の泥
水、例えば下水処理汚泥の固液分離等にも適用できるも
のであることは当業者にとって容易に理解できるところ
である。
In the vehicle-mounted mobile waste mud treatment device 14 shown in FIG. 2, the waste mud discharged from the waste mud storage tank 1 is mixed with the A coagulant in the static mixer 4, and then in the mixing pipe 6. The flocculant B is added at 1, then introduced into the inlet of the wound hose floc generator 8 and slowly passed through the hose. In the hose, the floc formation reaction is promoted, the flocs generated in the hose grow sufficiently in the hose, and in the outlet hose, flocs and free water are well separated and led out of the system. Then, it is supplied to the gravity dehydrator 9 and separated into flocs and separated water, and the flocs remaining on the mesh belt of the gravity dehydrator are transferred to the belt press type dehydrator 10 and further dehydrated to form a dehydrated cake, which is dehydrated. The cake is loaded on the waste transfer vehicle 13 such as a dump truck by the belt conveyor 11. The separated water derived from the mesh belt type dewatering device 9 and the separated water derived from the belt press type dewatering device 10 are introduced into the adjusting tank 12, where p
After H measurement and SS measurement, neutralization by addition of acid, alkali and the like and removal of SS content by addition of coagulant are achieved, the product is discharged into sewage. It is easily understood by those skilled in the art that the solid-liquid separation treatment method and treatment apparatus of the waste mud water of the present invention described above can be applied to other mud water, for example, solid-liquid separation of sewage treatment sludge. This is where you can do it.

【0010】[0010]

【発明の効果】上記のごとく本発明によれば、廃棄泥水
の固液分離処理を、簡易構造で構成でき、敷地面積も少
なくてすみ、連続処理によって処理時間も少なくてす
み、そして設備費用も少なくして実施することが可能と
なり、工業的に極めて有利なものとなる。特に、車載型
移動式の廃棄泥水処理装置を構成することもでき、随時
建設現場等へ同装置を移動し、その場で廃棄泥水を処理
できるので、機動性に優れ、かつ設備設置コストも非常
に低くすることができる。
As described above, according to the present invention, the solid-liquid separation treatment of waste mud water can be constituted by a simple structure, the site area is small, the treatment time is small by continuous treatment, and the facility cost is also low. It can be carried out with a small amount, which is extremely advantageous industrially. In particular, it is possible to configure an on-vehicle mobile waste muddy water treatment device, which can be moved to a construction site or the like at any time, and waste muddy water can be treated on the spot. Can be lowered to

【図面の簡単な説明】[Brief description of drawings]

【図1】廃棄泥水処理装置の概説図[Figure 1] Schematic diagram of waste mud treatment equipment

【図2】廃棄泥水処理装置を車載した概説図[Fig. 2] Schematic diagram of a vehicle equipped with a waste mud treatment device

【符号の説明】[Explanation of symbols]

1:廃棄泥水貯留槽 2:流量調整弁 3:流量計 4:スタチックミキサー 5:凝集剤槽(A剤槽) 6:混合管 7:凝集剤槽(B剤槽) 8:巻回ホースフロック生成装置 9:重力脱水装置 10:ベルトプレス型脱水装置 11:ベルトコンベア 12:調整槽 13:ダンプ車 14:移動式廃棄泥水処理装置 1: Waste muddy water storage tank 2: Flow rate control valve 3: Flow meter 4: Static mixer 5: Flocculant tank (A agent tank) 6: Mixing pipe 7: Flocculant tank (B agent tank) 8: Winding hose flock Generation device 9: Gravity dewatering device 10: Belt press type dewatering device 11: Belt conveyor 12: Adjustment tank 13: Dump truck 14: Mobile waste mud treatment device

───────────────────────────────────────────────────── フロントページの続き (72)発明者 岸野 富夫 東京都港区芝浦一丁目2番3号 清水建設 株式会社内 (72)発明者 飯塚 芳雄 東京都港区芝浦一丁目2番3号 清水建設 株式会社内 ─────────────────────────────────────────────────── ─── Continued Front Page (72) Inventor Tomio Kishino 1-3-2 Shibaura, Minato-ku, Tokyo Shimizu Construction Co., Ltd. (72) Inventor Yoshio Iizuka 1-3-2 Shibaura, Minato-ku, Tokyo Shimizu Construction Within the corporation

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】廃棄泥水に凝集剤を添加混合した後、それ
を巻回ホース中に導入し、同ホース内で生成するフロッ
クをゆっくりと撹拌しながら滞留させ、水との分離を促
進させることを特徴とする廃棄泥水処理方法。
1. A coagulant is added to and mixed with waste mud water, which is then introduced into a winding hose so that flocs generated in the hose are slowly agitated and retained to promote separation from water. A method for treating waste mud water, which is characterized by:
【請求項2】巻回ホースが、渦巻き状ホースであること
を特徴とする請求項1記載の廃棄泥水処理方法。
2. The waste mud treatment method according to claim 1, wherein the wound hose is a spiral hose.
【請求項3】巻回ホースが、立体的に巻回してなるもの
であり、廃棄泥水を巻回ホースの入口部より供給するこ
とを特徴とする請求項1又は2記載の廃棄泥水処理方
法。
3. The waste mud treatment method according to claim 1, wherein the winding hose is three-dimensionally wound, and the waste mud is supplied from the inlet of the winding hose.
【請求項4】巻回ホースよりなるフロック生成装置を備
えてなることを特徴とする廃棄泥水処理装置。
4. A waste muddy water treatment device comprising a floc generation device composed of a wound hose.
【請求項5】巻回ホースが、渦巻き状ホースであること
を特徴とする請求項4記載の廃棄泥水処理装置。
5. The waste mud treatment device according to claim 4, wherein the winding hose is a spiral hose.
【請求項6】巻回ホースが、立体的に巻回してなるもの
であり、廃棄泥水が巻回ホースの入口部より供給される
ことを特徴とする請求項4又は5記載の廃棄泥水処理装
置。
6. The waste mud treatment device according to claim 4, wherein the winding hose is three-dimensionally wound, and the waste mud is supplied from the inlet of the winding hose. .
【請求項7】請求項4ないし6のいずれかに記載の廃棄
泥水処理装置を備えてなることを特徴とする移動式廃棄
泥水処理装置。
7. A mobile waste muddy water treatment apparatus comprising the waste muddy water treatment apparatus according to any one of claims 4 to 6.
【請求項8】請求項4ないし6のいずれかに記載の廃棄
泥水処理装置を備えてなることを特徴とする車載型移動
式廃棄泥水処理装置。
8. An on-vehicle mobile waste muddy water treatment apparatus comprising the waste muddy water treatment apparatus according to any one of claims 4 to 6.
JP12033896A 1996-05-15 1996-05-15 Waste muddy water treatment and device therefor Pending JPH09299712A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12033896A JPH09299712A (en) 1996-05-15 1996-05-15 Waste muddy water treatment and device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12033896A JPH09299712A (en) 1996-05-15 1996-05-15 Waste muddy water treatment and device therefor

Publications (1)

Publication Number Publication Date
JPH09299712A true JPH09299712A (en) 1997-11-25

Family

ID=14783788

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12033896A Pending JPH09299712A (en) 1996-05-15 1996-05-15 Waste muddy water treatment and device therefor

Country Status (1)

Country Link
JP (1) JPH09299712A (en)

Cited By (12)

* Cited by examiner, † Cited by third party
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JP2002205099A (en) * 2001-01-10 2002-07-23 Japan Steel & Tube Constr Co Ltd Sludge treatment equipment and sludge treatment method
JP2005013778A (en) * 2003-06-23 2005-01-20 Toa Harbor Works Co Ltd Cleaning method of muddy water
JP2005036517A (en) * 2003-07-15 2005-02-10 Penta Ocean Constr Co Ltd Shield-excavated soil dehydrating method
JP2006167583A (en) * 2004-12-15 2006-06-29 Taiheiyo Cement Corp Sludge treatment method, sludge treating system, and flocculant addition apparatus for sludge
JP2008229487A (en) * 2007-03-20 2008-10-02 Taiheiyo Cement Corp Construction sludge volume reduction device, and construction sludge volume reduction method
JP2009113036A (en) * 2007-11-07 2009-05-28 Palo Alto Research Center Inc Dynamic processing system for water purification and method for dynamic processing in water purification
US8276760B2 (en) 2006-11-30 2012-10-02 Palo Alto Research Center Incorporated Serpentine structures for continuous flow particle separations
CN103007592A (en) * 2011-09-20 2013-04-03 北京朗新明环保科技有限公司 Clarifier
JP2015040728A (en) * 2013-08-21 2015-03-02 株式会社リソースクリエイト Mobile type compact decontamination device
JP2016047506A (en) * 2014-08-28 2016-04-07 株式会社奥村組 Mobile muddy water treatment equipment
CN107381988A (en) * 2017-08-16 2017-11-24 山东大学 A kind of shield high concentration discards mud disposal system and method
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Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002205099A (en) * 2001-01-10 2002-07-23 Japan Steel & Tube Constr Co Ltd Sludge treatment equipment and sludge treatment method
JP2005013778A (en) * 2003-06-23 2005-01-20 Toa Harbor Works Co Ltd Cleaning method of muddy water
JP2005036517A (en) * 2003-07-15 2005-02-10 Penta Ocean Constr Co Ltd Shield-excavated soil dehydrating method
JP2006167583A (en) * 2004-12-15 2006-06-29 Taiheiyo Cement Corp Sludge treatment method, sludge treating system, and flocculant addition apparatus for sludge
US8276760B2 (en) 2006-11-30 2012-10-02 Palo Alto Research Center Incorporated Serpentine structures for continuous flow particle separations
JP2008229487A (en) * 2007-03-20 2008-10-02 Taiheiyo Cement Corp Construction sludge volume reduction device, and construction sludge volume reduction method
SG152214A1 (en) * 2007-11-07 2009-05-29 Palo Alto Res Ct Inc Device and method for dynamic processing in water purification
JP2009113036A (en) * 2007-11-07 2009-05-28 Palo Alto Research Center Inc Dynamic processing system for water purification and method for dynamic processing in water purification
US9862624B2 (en) 2007-11-07 2018-01-09 Palo Alto Research Center Incorporated Device and method for dynamic processing in water purification
US10052571B2 (en) 2007-11-07 2018-08-21 Palo Alto Research Center Incorporated Fluidic device and method for separation of neutrally buoyant particles
CN103007592A (en) * 2011-09-20 2013-04-03 北京朗新明环保科技有限公司 Clarifier
JP2015040728A (en) * 2013-08-21 2015-03-02 株式会社リソースクリエイト Mobile type compact decontamination device
JP2016047506A (en) * 2014-08-28 2016-04-07 株式会社奥村組 Mobile muddy water treatment equipment
CN107381988A (en) * 2017-08-16 2017-11-24 山东大学 A kind of shield high concentration discards mud disposal system and method

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